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Amphibian and Reptile 

Surveys on 

Montana Refuges: 

1998 - 1999 



A Report to the 
U.S. Fish and Wildhfe Service: 

Montana Field Office 

CM. Russell National Wildlife Refuge 

Medicine Lake National Wildlife Refuge 



Submitted by 
Paul Hendricks 

December, 1999 




M o s T A ^■ .^ 



NatuoJ Heritage 
Program 



© 1999 Montana Natural Heritage Program 

1515 East Sixth Avenue, P.O. Box 201800, Helena, MT 59620-1800 



This document should be cited as follows: 

Hendricks, P. 1999. Amphibian and reptile surveys on Montana refuges: 1998-1999. Montana Natural Heritage 
Program. Helena, MT. 22 pp. 



ABSTRACT 

A total of 1 9 site surveys for amphibians and reptiles was conducted at 1 5 National Wildlife 
Refuge (NWR) and Waterfowl Production Area (WPA) "units" in 1 998- 1 999 in central and eastern 
Montana. Sites were chosen to augment data already available on these Fish and Wildlife Service units 
in the Montana Natural Heritage Program databases, to fill distribution gaps, and to visit sites where 
species rare in Montana were reported previously. No sites were visited more than twice, however, 
thus species tallies for each site are incomplete. Surveys, made by one individual, focused on wetlands, 
such as ponds, lakes, streams or seeps. Because of this habitat focus, reptiles especially were 
underrepresented in the results, unless associated with wetland sites. Surveys lasted 1 5-240 minutes, 
depending on site conditions and/or size. Opportunistic observations made in the region during field 
work, along with sightings reported by USF WS personnel, are included in this report. 

Four amphibian and three reptile species total were detected on 12 site surveys at 9 units. The 
species detected included Tiger Salamander (Ambystoma tigrinum) on 1 survey (1 unit). Western 
Chorus Frog (Pseudacris triseriata) on 4 surveys (3 units), Woodhouse's Toad {Bufo woodhousii) on 
2 surveys (2 units). Northern Leopard Frog {Ranapipiens) on 4 surveys (3 units). Painted Turtle 
{Chrysemys pictd) on 1 survey (1 unit). Racer {Coluber constrictor) on 1 survey (1 unit), and Plains 
Garter Snake {Thamnophis radix) on 3 surveys (2 units). Refuge personnel contributed several 
records of opportunistic encounters for species not detected during surveys at one unit (Medicine Lake 
NWR), and at one other unit (Bowdoin NWR) where site surveys were not conducted. Seven 
additional site surveys and 4 opportunistic observations in the vicinity of several units (but not on 
USFWS lands) indicated the likely occurrence of some species on refuge units where they were not 
detected. 



TABLE OF CONTENTS 

ABSTRACT i 

ACKNOWLEDGMENTS iv 

INTRODUCTION 1 

METHODS AND MATERIALS 3 

Figure 1. USFWS Units visited 1998-1999 4 

RESULTS AND DISCUSSION 5 

General Summary 5 

USFWS Unit Accounts 6 

RECOMMENDATIONS 10 

BIBLIOGRAPHY 12 

APPENDIX 1. SITES SURVEYED 21 

APPENDIX 2. SPECIES DETECTED ON SURVEYS 22 



ACKNOWLEDGMENTS 



Thanks to Martin Miller for data entry and Cedron Jones for producing the map. Financial 
support for the proj ect came from Challenge Cost-Share Agreement No. 1 448-60 1 8 1 -98- J3 80 
between the U.S. Fish and Wildlife Service and the Montana Natural Heritage Program. 
Museum records of Montana amphibians and reptiles were received from over 20 institutions (a list is 
available in previous reports on amphibian and reptile surveys). These important records form the 
historical base from which changes in abundance and distribution can be identified. Most museum data 
were received with the help of Dr. Charles Peterson, Idaho State University, Pocatello. Other records 
pertinent to this report and period of study were made available by Dr. Kirwin Werner (Ronan), Ted 
Nordhagen (Westby), Frank Durbian (Bowdoin NWR), and Beth Madden (Medicine Lake NWR). 



IV 



INTRODUCTION 



Populations of several amphibian species are currently declining in the western U.S. and 
elsewhere around the world. Acid rain, ozone depletion, pollution by toxic chemicals and heavy metals, 
predation and/or competition by exotic species, habitat alteration, climatic changes, disease, immune 
system problems, and combinations of several of these factors have all been suggested as possible 
causes (Com and Fogelman 1 984, Phillips 1 990, Yoflfe 1 992). Recognition of these alarming 
population trends has renewed interest in the status amphibian populations in particular, and raised 
awareness regarding current ignorance of the status of many reptile species as well. 

The amphibians and reptiles occupying the plains of eastem Montana have received scant 
attention by naturalists and biologists. As a consequence, we know very little about the status, 
population trends, habitat requirements, and reproductive biology of many species within this region of 
the state. With new information acquired in the last 5 years from a series of regional inventories of the 
herpetofauna in eastem Montana (e.g., Reichel 1 995b, Hendricks and Reichel 1 996, Hendricks and 
Reichel 1 998, Roedel and Hendricks 1 998, Hendricks 1 999), we are gaining an understanding of 
abundance and population trends for several species. In addition, we are "fleshing ouf known 
distributions that were largely based on opportunistic encounters and other data at least half a century 
old. 

In 1 805-1 806 Lewis and Clark were the first to document the presence of Spiny Softshell 
(Trionyx spiniferus), Eastem Short-homed Lizard {Phrynosoma hernandezi), Westem Terrestrial 
Garter Snake {Thamnophis elegans), and Western Rattlesnake {Crotalis viridis) along the Missouri 
River in present-day eastem Montana (Burroughs 1 995). Most additional published accounts of 
amphibians and reptiles in eastem Montana are concentrated along the Missouri River corridor and its 
tributaries. Notable among these reports is that of Cope (1 879), who commented on the occurrence of 
5 amphibian and 3 reptile species between the Judith River and Armells Creek. More recently, 
Mosimann and Rabb (1 952) documented the presence of 4 amphibian and 7 reptile species in the Tiber 
Reservoir area along the Marias River of northcentral Montana. The written record of exploration of 
Montana in the 1 9^^ century and first half of the 20^^ century, and unpublished museum collection 
records, provide the base for analyses of historical distributions and population trends. Additional 
distribution and status information for border regions can be gleaned from Wheeler and Wheeler (1 966) 
for North Dakota, Visher (1914) for South Dakota, Baxter and Stone (1985) for Wyoming, and Secoy 
and Vincent (1 976) for Saskatchewan. 

Preliminary data gathered from site surveys and revisits to historical sites indicate that the 
Northern Leopard Frog {Ranapipiens) has disappeared over much of its former range in westem 
Montana (Werner et al. 1 998) and is declining in at least some areas of eastem Montana. Status and 
population trend of several toad species {Bufo spp.) are unknown, although declines of the Westem 
Toad {Bufo boreas) have been reported recently in northern Idaho (C. Peterson pers. comm.), 
northwestern Montana (Werner and Reichel 1 994, Werner et al. 1 998), Yellowstone National Park 
(Koch and Peterson 1995) and Colorado (Carey 1993). 



Land-use practices, such as large-scale logging, continue to be detrimental to resident 
amphibians in some regions ofthe western U.S. (Buryetal. 1991). The impacts of grazing on 
amphibians and reptiles and their habitats remain poorly studied and understood. Heavy grazing in and 
around breeding sites associated with water may negatively impact amphibians and reptiles by 1 ) 
eliminating emergent vegetation necessary for egg and larval survival, 2) lowering water quality, 
especially causing high siltation levels, 3) trampling of eggs, larvae and adults, and 4) degrading the 
amphibian and reptile food base. Additionally, modification of seeps and springs for livestock watering, 
by capturing water flow in tanks, may make former breeding sites unusable by amphibians. 

The Montana Natural Heritage Program currently lists five amphibian and five reptile species as 
Animal Species of Special Concern (Roedel 1999). Of these, two amphibian and five reptile species 
have been documented in eastern Montana. They are Canadian Toad {Bufo hemiophrys). Northern 
Leopard Frog {Ranapipiens\ Common Snapping Turtle {Chelydra serpentina\ Spiny Softshell 
(Trionyx spiniferus). Western Hognose Snake {Heterodon nasicus). Milk Snake {Lampropeltis 
triangulum), and Smooth Green Snake {Liochlorophis [=Opheodrys] vernalis). Most ofthe above 
species are of special concern because of limited distributions or relatively few records in recent years, 
but there is evidence of a significant decline in Northern Leopard Frog populations in the last 3 years in 
western and central portions ofthe state. The species is now listed as Sensitive by the U.S. Forest 
Service, Region 1 . 

In 1998-1999, several refuge "units" under stewardship ofthe U.S. Fish and Wildlife Service 
(Refuges and Waterfowl Production Areas) were visited and surveyed briefly for amphibians and 
reptiles. Obj ectives ofthe work presented in this report were to 1 ) augment data already available on 
these Fish and Wildlife Service units in the Montana Natural Heritage Program databases, 2) fill 
distribution gaps, and 3) visit sites where species rare or of special concern in Montana were reported 
previously. 



METHODS AND MATERIALS 

Seven National Wildlife Refuges (Medicine Lake, Charles. M. Russell, Lake Mason, War 
Horse, Hailstone, Halfbreed, Lame Steer) in central and eastern Montana were visited, and site surveys 
were conducted of all or portions of each in 1 998- 1 999. Records from 1 999 were also received from 
USFWS personnel at Medicine Lake and Bowdoin NWR's; the latter was not visited during this 
inventory. In addition, six Waterfowl Production Areas (Tew, Spidell, Clarks Fork, Flaxville, Jagiello, 
International [Outlet] Marsh) were visited and surveyed, at least in part. 

Historical records from museum collections can be very usefiil in determining long-term changes 
in populations or shifts in biodiversity (Shaffer et al. 1 998). Historical locations of amphibians and 
reptiles were recorded from the literature (see Bibliography) and museum specimen records. Records 
were received from over 20 maj or North American museums that have computerized their collection 
records (see Acknowledgments). Locations derived from these sources have been entered into a 
database and digitized. 

Survey sites (n = 1 9) were chosen based on 3 criteria: 1 ) few or no previous surveys by 
MTNHP zoologists, 2) location of reservoirs and ponds, streams, seeps and wetlands on topographic 
maps, and 3) accessibility of the wetlands by roads. From 1 5-240 minutes were spent during each site 
survey (mean = 57.1 minutes), depending upon the size of the area, site conditions, and what was 
found. Initially, the shoreline or wetland margin was searched by walking slowly along the edge and up 
into the surrounding vegetation, including rolling over rocks and logs. At regular intervals, the aquatic 
habitat was sampled for tadpoles or larvae using a dipnet. If the initial sampling showed amphibian/ 
reptile species present, further effort was expended in order to get a more comprehensive view of 
abundance and distribution. 

An attempt was made to capture at least the first few individuals of a species seen at a survey 
site. The species name was recorded along with developmental stage and sex (if possible); the animals 
were then released. On occasion, representative samples of the more common species in an area were 
preserved for permanent museum records and will be deposited at the Idaho State University Museum. 
Water temperature, air temperature, and a general description of the area were recorded. Standardized 
data sheets were used during this project; the amphibian survey data sheet was developed by U.S. Fish 
and Wildlife Service and is used extensively by a variety of researchers in the western U.S. Much site- 
specific data was gathered during these surveys; not all data has been analyzed or is presented in this 
report, but is available upon request from the Montana Natural Heritage Program. 



Figure 1. U.S. Fish and Wildlife Service refuges and waterfowl production areas visited during 
1998-1999 site surveys. 

USFWS refuge and waterfowl production areas visited: 1 998-1 999 



International (Outlet^ MarRh WPA 
• JagifelloWPA | 



► Flaxville WPA 




Medicine Lake NV^m^' 



.^ 



y'-i.^-v^'^' 



^-^.JIa 



[ ^War Horse NVJ/R <War Horse Lake) 
I ^ War Horse MWR (Yellow Water Res.) 



Lake Mason NWR c 



W- 



^ *Te\A^WPA 
""[^SprdelWPA 
• Hailstone NWR 
•HalfbreedNWR /" 



1 ,...y' 



) 



iCIarks Fork WPA 




I ./■■■■ 



-:ii- 






Lamesjteer NWR* 



? I 



10 20 30 40 50 

r-^ V////A Km 



Scale in Miles 



MTNHP. November 03. 1999 



RESULTS AND DISCUSSION 

General Summary 

A total of 1 9 site surveys was conducted in May- July 1 998 and June 1 999 (Appendix 1 ), on 1 2 
of which one or more species of amphibian or reptile were present. Localized sites encompassing a 
wide range in land area across much of central and eastern Montana were covered in the inventory 
(Figure 1). Included were visits to 1 5 "units at seven National Wildlife Refuges (NWR's) and six 
Waterfowl Production Areas (WPA's); two of the NWR's visited included two discrete management 
units each (see USFWS Unit Accounts). No species were found on seven site surveys. On four of 
these, basins containing water were completely or mostly dry at the time of the survey, so chances of 
detecting any species were greatly diminished and largely dependent upon locating snakes which, 
barring fortuitous encounters, often require labor-intensive searches. During the other three site surveys, 
failure to detect any species may have been due to the time of day, weather conditions, or other factors 
(including length of search and size of search area) at the time of sampling. It is recommended that lentic 
sites (ponds, reservoirs, marshes, etc) be sampled more than once during a breeding season to increase 
the likelihood of detecting rare, cryptic, and later or earlier-breeding species (Thoms et al. 1 997). This 
was not done at several locations for logistical reasons, but is the recommended procedure for future 
survey efforts. 

Four amphibian and three reptile species were detected on 12 site surveys at 9 USFWS 
administered units during the 1 998-1 999 inventory (Appendix 2). Amphibian and reptile species, and 
number of surveys and WPA/NWR units where detected, included Tiger Salamander (Ambystoma 
tigrinum) on 1 survey (1 unit). Western Chorus Frog {Pseudacris triseriata [= maculata]) on 4 
surveys (3 units), Woodhouse's Toad (Bufo woodhousii) on 2 surveys (2 units). Northern Leopard 
Frog {Ranapipiens) on 4 surveys (3 units). Painted Turtle {Chrysemys picta) on 1 survey (1 unit). 
Racer (Coluber constrictor) on 1 survey (1 unit), and Plains Garter Snake (Thamnophis radix) on 3 
surveys (2 units). No species were detected on 7 site surveys, one species on 8 site surveys, and two 
species on 4 site surveys. 

No species were detected during site surveys at 6 units (HalfbreedNWR, Lake Mason NWR 
[Lake Mason and Willow Creek units]. Medicine Lake NWR, Tew WPA, Spidell WPA). One species 
was detected at 5 units (Charles M. Russell NWR, Hailstone NWR, Flaxville WPA, International [= 
Outlet] Marsh WPA, Jagiello WPA), two species at 3 units (Lame Steer NWR, War Horse Lake 
NWR [War Horse Lake and Yellow Water Reservoir units]), and three species at 1 unit (Clarks Fork 
WPA). 

Opportunistic sightings from MTNHP and refuge personnel in 1 998- 1 999 on or near USFWS 
units added five species (all snakes) not reported during site surveys: Smooth Green Snake 
{Liochlorophis vernalis). Gopher Snake (Pituophis catenifer). Common Garter Snake {Thamnophis 
sirtalis). Western Terrestrial Garter Snake {Thamnophis elegans), and Western Rattlesnake {Crotalus 
viridis). In addition to the 1 9 site surveys on USFWS units, there were eight MTNHP site surveys in 
late June-early July 1 998 on other public lands (all BLM); seven surveys were in Musselshell County 
from near Roundup to the Lake Mason NWR vicinity, and one survey was north of Winnett in 
Petroleum County. Results of these eight surveys included Tiger Salamander at 2 sites. Western Chorus 
Frog at 7 sites. Northern Leopard Frog at 2 sites, and Plains Garter Snake at 4 sites. 



The following accounts are organized by USFWS unit, beginning withNWR's (including one 
not surveyed by MTNHP during 1 998- 1 999) and followed by WPA's (again, including one not 
surveyed in 1 998- 1 999). Included in each account are a description of the 1 998- 1 999 survey results 
and a summary of species previously documented from each unit and in the MTNHP databases in 
Helena. 

USFWS Unit Accounts 

Bowdoin National Wildlife Refuge . No surveys were conducted at this unit in 1 998- 1 999. However, 
five species were reported in 1 999 by refuge personnel from various sections on the refuge. These 
included Tiger Salamander (1 adult in the Dry lake unit on 23 June, 1 adult on the west side of Lake 
Bowdoin in 1 October), Gopher Snake (1 at Black Coulee Inlet on 5 May), Racer (1 near the shop 
building on 27 June, 1 ca. 3 miles NE of Headquarters on 28 June), Common Garter Snake (1 on 1 5 
August on the east side of Drumbo), and Plains Garter Snake (1 on 27 June near the shop, 1 on 1 5 
August on the east side of Drumbo). There are records of three additional species from this unit in the 
MTNHP databases: Western Chorus Frog, Painted Turtle, Western Rattlesnake (see Hendricks and 
Reichell998). 

Charles M. Russell National Wildlife Refuge . One survey was conducted on this refuge during 1 998- 
1 999; one species was detected. Woodhouse's Toad (ca. 200+ tadpoles with no or early hind limb 
buds) was observed near the confluence of Crooked Creek and Fort Peck Reservoir on 1 9 June 1 999. 
There are records of 1 1 additional species from throughout this refuge in the MTNHP databases: Tiger 
Salamander, Western Chorus Frog,, Great Plains Toad {Bufo cognatus). Northern Leopard Frog, 
Painted Turtle, Spiny Softshell (Trionyx spiniferus\ Racer, Gopher Snake, Western Hognose Snake 
(Heterodon nasicus). Common Garter Snake, Western Rattlesnake (see Hendricks and Reichel 1 998). 

Hailstone National Wildlife Refuge . One survey was conducted on this refuge in 1 999, on 5-6 June. 
Only one species was detected during four hours of survey effort and an overnight stay. A single adult 
(total length = 60 cm) Racer was found dead along the outlet creek. No frogs or toads were seen or 
heard. There are no records of other species at this unit in the MTNHP databases. 

Halfbreed National Wildlife Refuge . One survey was conducted on this refuge in 1 999, on 5 June. No 
amphibian or reptile species were found, but only a small section was surveyed. There are records of 
two species (Tiger Salamander, Western Rattlesnake) at this unit in the MTNHP databases. 

Lake Mason National Wildlife Refuge (Lake Mason unit) . One survey was conducted on this refuge 
unit in 1 999, on 6 June. The lake bed was mostly dry. No amphibian or reptile species were detected. 
There are no records of amphibians or reptiles from this refuge unit in the MTNHP databases. 
However, a survey of a reservoir in Tl 0NR24ES3 INE, 5 mi. NW of Lake Mason (on BLM land), 
detected 50-1 00 adult Western Chorus Frogs on 21 June 1 998. Also, Northern Leopard Frogs (3 
adults, 2 juveniles) were encountered on 21 June 1 998 during a survey on Willow Creek (which drains 
into Lake Mason) on BLM land in T 1 0NR24ES 1 7NW, about 7 mi. NNW of Lake Mason. 



Lake Mason National Wildlife Refuge (Willow Creek unit) . One survey was conducted in this unit in 
1 999, on 6 June. Minerva Creek was dry, no amphibian or reptile species were detected. There are 
no records of amphibian or reptile species from this unit. However, a road-killed adult (total length = 
80 cm) Plains Garter Snake was seen on 6 June on the Snowy Mountain Road about 4 mi. SE of this 
unit (Tl 0NR23ES 1 INWSE), and a road-killed Gopher Snake was observed about 7 mi. NE of this 
unit (Tl 1NR24ES5NESE) on the same date. 

Lame Steer National Wildlife Refuge . One survey was conducted on this refuge in 1 998, on 23 July. 
One amphibian and one reptile species were detected at this unit. Northern Leopard Frogs were 
collected within 4 miles of this site in 1 91 5, and the species is still present. Leopard frogs (2 adults, 12 
juveniles mostly 4-5 cm snout- vent length) were found below the dam, and in the emergent vegetation in 
the upper (east) end of the reservoir. One Plains Garter Snake (juvenile) was seen in emergent 
vegetation along the reservoir above the dam. A local farmer reported Painted Turtles (not seen during 
the survey) in the reservoir and Common Snapping Turtle in nearby Beaver Creek (also not seen during 
the survey). There are no records of additional amphibian or reptile species from this unit in the 
MTNHP databases. 

Medicine Lake National Wildlife Refuge . One survey was conducted on this refuge (a marsh near the 
entrance, in section 3 INWNW) in 1 998, on 3 1 May. No amphibian or reptile species were detected. 
However, Painted Turtle (2 adults) was noted in T32NR57ES32SES W on 30 May 1 998, and a road- 
killed Gopher Snake was seen W of Froid near Big Muddy Creek N of Johnson Lake 
(T30NR55ES2 1 S WNE) on 28 May 1 998. Refuge personnel reported five species in 1 999 (two 
amphibian, 2 reptile): Tiger Salamander (Big Island Pelican Colony; thousands regurgitated to chicks in 
July and August), Northern Leopard Frog (refuge headquarters on 27 September, many other localities 
and dates). Smooth Green Snake (Bridgerman Point in May- June, Headquarters on 25 June and 
August-September, T3 1 WR55ES21 on 13 May, Medicine Lake School football field [off-refuge] in 
September), and Western Terrestrial Garter Snake (several observations in 1998 and 1999). An 
unidentified toad (possibly Woodhouse's Toad) was also noted at headquarters. There are records of 
two additional species from this refuge (Racer, Western Hognose Snake) in the MTNHP databases. 
There are also records of Northern Leopard Frog for this unit from 1 942, and the species is still 
present. 

War Horse National Wildlife Refuge (War Horse Lake unit) . Three surveys were conducted at this unit 
in 1 998- 1 999. No amphibians or reptiles were detected on 27 May 1 998 along the southern shoreline 
(no emergent vegetation). Western Chorus Frogs (10+ calling adults) were present on 3 1 May 1 998 
along the inlet canal. Northern Leopard Frogs (3 juveniles 4.0 cm snout- vent length) were in a small 
stock pond near the inlet canal, and 2 tadpoles (4.0 and 4.5 cm total length) were captured in the inlet 
canal proper on 20 June 1 999. There are records of one additional amphibian species (Plains 
Spadefoot, Spea bombifrons) from this unit in the MTNHP databases. A Western Rattlesnake was 
seen about 8 mi. E of this unit on the Valentine-Dovetail Road (T 1 6NR26ES INENE) on 2 1 June 1 999, 
and a Racer was seen a few miles farther (on Dovetail Road) on the same date. 

War Horse National Wildlife Refuge (Yellow Water Reservoir unit) . Two site surveys were conducted 
at this unit during 1 998- 1 999. One amphibian and one reptile species were detected. Northern 
Leopard Frog was reported at this unit in 1 950 and was still present. One adult was noted in the 
outflow marsh below the dam on 27 May 1 998. Plains Garter Snake was noted on 27 May 1 998 (1 
adult in the marsh below the dam) and 1 8 June 1 999 (1 adult along the outflow ditch below the dam). 



There are records of one additional amphibian species (Western Chorus Frog) from this unit in the 
MTNHP databases. 

Clarks Fork Waterfowl Production Area . Two site surveys were conducted at this unit in 1 999, on 1 5 
and 23 June. Two amphibian and one reptile species were detected: Western Chorus Frog ( 2 calling 
adults in the pond near the parking area on 1 5 June, 1 in the same ponds and the main marsh on 23 
June), Woodhouse's Toad (3 adults, 6-8 cm snout- vent length; 50+ tadpoles 3 cm total length, all in the 
main marsh on 23 June), Painted Turtle (1 adult in gravel pond close to parking area on 1 5 June). The 
toad and turtle records are the first reported for Carbon County. There are no records of additional 
amphibian or reptile species for this unit in the MTNHP databases. 

Erickson Waterfowl Production Area . This unit near Medicine Lake NWR was not surveyed in 1 998- 
1 999. However, a juvenile Smooth Green Snake (about 24 cm total length), apparently killed during a 
hail storm, was reported on 7 July 1 998 by Lance Tanino, and is the first specimen of this species 
collected in Montana. There are no other records of amphibians or reptiles for this unit in the MTNHP 
databases. 

Flaxville Waterfowl Production Area . One site survey was conducted at this unit in 1 998, on 29 May. 
One amphibian species was observed. Northern Leopard Frog (3 juveniles ca. 4 cm snout- vent length) 
were seen in two areas: one N of Highway 5, and two in emergent vegetation on the W side of the 
pothole S of the highway. There is a record of one additional amphibian species, Canadian Toad {Bufo 
hemiophrys\ from this unit in the MTNHP databases. This record (30 July 1 966) is the only confirmed 
report for Montana (see Black and Bragg 1 968). The species was not seen during the 1 998 survey, but 
the site merits additional surveys. 

International (Outlet) Marsh Waterfowl Production Area . One site survey was conducted at this unit in 
1 998, on 29 May. One amphibian species was observed. Tiger Salamander (1 large larva ca. 1 3 cm 
total length) was observed in the outlet stream draining the marsh. Large portions of the marsh were not 
surveyed, and the site merits additional survey effort. There are no records of additional amphibian or 
reptile species from this unit in the MTNHP databases. 

Jagiello Waterfowl Production Area . One site survey was conducted at this unit in 1 998, on 29 May. 
One amphibian species was observed. Western Chorus Frog (4 adults, 4 tadpoles 2-3 cm total length) 
were detected in emergent vegetation in the southern half of this pothole. This site merits additional 
surveys. There are no records of additional amphibian or reptile species from this unit in the MTNHP 
databases. 

Spidell Waterfowl Production Area . One site survey was conducted at this unit in 1 999, on 6 June. No 
amphibian or reptile species were observed. The lakebed was completely or nearly dry, and no 
amphibians were seen or heard in the small water bodies along the road. There are no records of any 
amphibian or reptile species from this unit in the MTNHP databases. This unit should be resurveyed 
when water is present. 



Tew Waterfowl Production Area . One site survey was conducted at this unit in 1 999, on 6 June. No 
amphibian or reptile species were observed. All potholes were completely dry, and no amphibians or 
reptiles were seen or heard in the small cattail marshes traversed. There are no records of any 
amphibian or reptile species from this unit in the MTNHP databases. This unit should be resurveyed 
when water is present. 



RECOMMENDATIONS 

Surveys and Research 

1) Incidental sightings of amphibians and reptiles from the different USFWS units should be recorded 
and forwarded to the Natural Heritage Program. Of particular interest are all observations and 
locations of breeding amphibians (tadpoles and/or eggs) and all reptiles. Use Reichel and Flath (1 995) 
as an identification aid. Vouchers of amphibian tadpoles can be sent to the Natural Heritage program 
for identification. The Natural Heritage website has an online form for submitting amphibian and reptile 
observation data at http://nris.mt.gov/mtnhp/index.html . 

2) Due to the time constraints and the large area covered in this survey, it should not be regarded as a 
definitive index of all the amphibians and reptiles or their presence on the surveyed units. The secretive 
habits of many amphibians and reptiles, and our lack of knowledge regarding their reproductive 
behavior make it difficult to assess their overall status. Sites surveyed should include multiple visits, 
preferably during different times of the year (for surveys) and in different years (for monitoring). We 
recommend that additional surveys be conducted. 

3) Long-term monitoring of typical marsh-pond habitats at several units should be established, especially 
where there has been prior survey effort. These monitoring sites permit assessment of population trends 
and breeding success of the more common species: Tiger Salamander, Western Chorus Frog, 
Woodhouse's Toad, Northern Leopard Frog, and Plains Garter Snake. Particular attention needs to be 
given to any toad and Northern Leopard Frog breeding sites found, as these species appear to be 
experiencing declines in abundance in many areas within Montana and in other regions. Life history and 
ecology of the amphibians in Montana is still poorly known for most species. Long-term monitoring will 
provide information on timing of breeding and habitat requirements needed for successful reproduction, 
as well as the kind of information needed for successful management of local populations. 

Management 

1 ) With an increasing number of amphibian species declining for a variety of reasons, it is reasonable to 
manage habitat to support them. While not all ways of preserving and protecting these species are 
currently known, several management actions could impact them negatively. Amphibians cannot 
survive without adequate breeding sites, and the type of water used is often species-specific. 

a) Stocking fish in ponds and reservoirs currently lacking fish, and in which amphibians breed, 
should be carefully evaluated. Fish introductions are thought to be a major factor negatively 
impacting amphibian populations in California (Hayes and Jennings 1 986, Fellers and Drost 

1 993, Drost and Fellers 1 996) and Oregon (Kiesecker and Blaustein 1 998). It may even be 
desirable to remove introduced fish from some water bodies. 

b) When altering springs and seeps for livestock, protect a portion of the area that is suitable for 
amphibian reproduction. This could include small fenced exclosures above water diversions to 
stock tanks; water from natural springs and seeps should not be diverted immediately into stock 
tanks, as this could exclude amphibians from access to the water. At sites with significant 
overfiow from wells and tanks, consider creating livestock exclosures along portions of the 
outfiow. Consider fencing off sections of ponds and reservoirs that include shoreline emergent 

10 



vegetation. This provides egg-laying sites and cover to immature amphibians, and also provides 
adults and immature stages with refugia from trampling by livestock. Exclosures at ponds and 
smaller reservoirs should be designed to account for water loss during evaporative drawdown, 
and encompass some water that will last at least to mid- August if possible. 

c) Create new ponds exclusively for amphibians to which livestock are excluded. Creation of 
buffer zones (Semlitsch 1 998) around these sites (and other sites as well) should also be 
considered, as the standing water in wetlands is used primarily for breeding and tadpole/larval 
development, not for much of adult activity by several species of semi-aquatic amphibians (such 
as Tiger Salamanders and the toads). Semi-aquatic species may disperse from large distances 
(> 2 km perhaps) to wetland sites to breed. Adult habitats also need to be considered in any 
active management program for amphibians. 

2) A critical component of the life cycle in snakes is the wintering den. Many species hibernate in large 
aggregations at traditional den sites. Often these hibemacula are used by more than one species 
(Koch and Peterson 1 995), and mating often takes place at or near the den site. Snakes then move 
away from dens for as much as 6 miles in summer, returning in the fall to over- winter. These sites 
typically are situated where snakes can get well down into an area of fractured rock, often near cliffs 
or in talus slopes. While these sites are robust, they are vulnerable to disturbance, such as road 
building, or vandalism and over-collecting. Den sites should be documented and protected. 
Fencing around dens might be suitable in some situations to exclude livestock. Sites should be 
monitored annually to determine use and relative abundance of species present. Den locations 
should be revealed only to responsible individuals. 

3) Traditional nesting sites of Common Snapping Turtles and Spiny Softshells, especially on the Charles 
M. Russell NWR where they are mostly likely to occur, should be protected from disturbance of 
any kind, through use of livestock exclosures if necessary. Most nesting sites, however, will be near 
larger rivers and tributaries in sandy and sand-deposition sites, and subjected to flooding and shifts 
in channels. Protection of individual nests may include establishing predator exclosures around 
clutches. This would be necessary only if it is evident that predators (skunks and raccoons in 
particular) are destroying an exceptional number of nests. Predation of turtle nests is often >50% in 
many areas, but "normal" predation rates for Montana populations are not known. 



11 



BIBLIOGRAPHY 

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12 



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14 



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15 



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16 



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17 



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18 



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19 



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20 



Appendix 1 . Site surveys by MTNHP for amphibian and reptiles during 1 998- 1 999 on USF WS units in Montana. 



SITE 



LOCATION 


ELEV. 


DAIE 


START TIME 


T20NR29ES36NWSW 


2250 


19Jun99 


11:05 


T3NR20ES13SW/S24NE 


4070 


5Jun99 


15:35 


T3NR21ES33SE 


3940 


5Jun99 


14:05 


T9NR24ES26NW 


3610 


6Jun99 


14:00 


T11NR23ES31NE 


3940 


6Jun99 


15:30 


T 1 2NR60ES 1 4S W/S 1 5N W 


2890 


23 Jul 98 


10:50 


T32NR56ES31NWNW 


1940 


31 May 98 


12:10 


T16NR25ES28SW 


3000 


27 May 98 


18:00 


T16NR25ES29NWNW 


3140 


31 May 98 


18:35 


T16NR25ES29NWNW 


3140 


20Jun99 


13:10 


T13NR26ES7SWNE 


3000 


27 May 98 


15:30 


T13NR26ES7SWNE 


3000 


18Jun99 


10:58 


T6SR23ES15NWSW 


3600 


15Jun99 


11:20 


T6SR23ES15NW 


3600 


23Jun99 


08:50 


T35NR50ES8SENE/SESE 


2750 


29 May 98 


12:40 


T37NR48ES1SENW 


2460 


29 May 98 


16:15 


T37NR49ES14SESE 


2460 


29 May 98 


14:50 


T5NR23ES33N 


3750 


6Jun99 


11:55 


T5NR25ES19NE/S20W 


3900 


6Jun99 


10:40 



Charles M. Russell NWR 

Hailstone NWR 

HalfbreedNWR* 

Lake Mason NWR (Lake Mason)* 

Lake Mason NWR (Willow Creek)* 

Lame Steer NWR 

Medicine Lake NWR* 

War Horse NWR (War Horse Lake)* 

War Horse NWR (War Horse Lake inlet) 

War Horse NWR (War Horse Lake inlet) 

War Horse NWR (Yellow Water Reservoir) 

War Horse NWR (Yellow Water Reservoir) 

ClarksForkWPA 

ClarksForkWPA 

FlaxvilleWPA 

International (Outlet) Marsh WPA 

JagielloWPA 

SpidellWPA* 

Tew WPA* 



Surveys with no amphibians or reptiles detected. 



21 



Appendix 2. Amphibian and reptile species detected during 1 998-1 999 surveys on USFWS units in Montana. 

SITE SEARCH (hrs:min) SPECIES (n = adult & juv.; * = eggs, larvae, tadpoles) 



Charles M. Russell NWR 

Hailstone NWR 

HalfbreedNWR 

Lake Mason NWR (Lake Mason) 

Lake Mason NWR (Willow Creek) 

Lame Steer NWR 

Medicine Lake NWR 

War Horse NWR (War Horse Lake) 

War Horse NWR (War Horse Lake inlet) 

War Horse NWR (War Horse Lake inlet) 

War Horse NWR (Yellow Water Reservoir) 

War Horse NWR (Yellow Water Reservoir) 

ClarksForkWPA 

ClarksForkWPA 

FlaxvilleWPA 

International (Outlet) Marsh WPA 

JagielloWPA 

SpidellWPA 

Tew WPA 



0:30 
4:00 
0:40 
0:30 
0:15 
1:00 
0:30 
0:40 
0:25 
0:30 
1:15 
1:00 
0:30 
2:00 
1:00 
0:35 
0:35 
0:20 
0:50 



BUWO (*) 

COCO (1) 

no herps 

no herps (dry) 

no herps (dry) 

RAPI(14),THRA(1) 

no herps 

no herps 

PSTR(10+) 

RAPI(3*) 

RAPI(1),THRA(1) 

THRA(l) 

PSTR(2),CHPI(1) 

PSTR(10),BUWO(3*) 

RAPI(3) 

AMTI(*) 

PSTR(4*) 

no herps (dry) 

no herps (dry) 



AMTI (Ambystoma tigrinum: Tiger Salamander), PSTR {Pseudacris triseriata: Western Chorus Frog), BUWO {Bufo woodhousii: Woodhouse's Toad), RAPI (Rana 
pipiens: Northern Leopard Frog), CHPI (Chrysemys picta: Painted Turtle), COCO (Coluber constrictor. Racer), THRA (Thamnophis radix: Plains Garter Snake). 



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